Land Use
Different land uses carry different risk assumptions. A residential site usually has stricter limits than an industrial property because people may live there long-term.
bccsrtool uses B.C.'s Contaminated Sites Regulation (CSR) Schedule 3.1 to compare individual soil measurements with applicable soil standards. Exceedances may warrant investigation or professional assessment. Schedule 3.1 provides matrix soil standards in Part 1 and generic human-health and ecological soil standards in Parts 2 and 3. This tool quickly screens the concentration thresholds of these chemicals & compares measured values against B.C.'s CSR Schedule 3.1.
bccsrtool screens mandatory and applicable soil factors. Unassessed factors and unsupported regulatory conditions remain inconclusive.
Before developing this tool, I completed a Phase I Environmental Site Assessment (ESA) project. While doing my research, I realised how tedious & complicated Schedule 3.1 was: matrix tables with eight site-specific factors, plus separate generic tables. Cross checking however many chemicals against however many standards would be a nightmare. There had to be a more straightforward way to do this.
bccsrtool was born. I wanted to streamline this process & also act as an educating tool. My goal was to build a straightforward screening tool that would allow users to quickly check Schedule 3.1 thresholds, compare the measured concentrations against the thresholds and understand the logic behind the thresholds. With this whole process done in just mere minutes.
Each step mirrors a small part of how early ESA information gets organized.
Different land uses carry different risk assumptions. A residential site usually has stricter limits than an industrial property because people may live there long-term.
Site history points toward likely contaminants. A former gas station suggests BTEX and petroleum VOCs; a dry cleaner suggests chlorinated solvents.
Enter soil concentrations in supported soil units. Non-detects and reporting limits need separate professional interpretation; do not enter them as zero.
The tool compares valid measurements with numeric thresholds and flags below, at threshold, exceeds, or review required.
Phase I observations rarely give a final answer, but they help narrow the first screening list.
BTEX and petroleum VOCs often become the first substances to check.
Why it matters: fuel releases can affect soil, groundwater, and vapour pathways.PCE/TCE chlorinated solvents are common screening candidates.
Why it matters: solvents can be mobile and persistent.PAHs, metals, and creosote-related contaminants may be relevant.
Why it matters: historical handling areas can leave mixed impacts.Metals and miscellaneous regulated substances are often worth reviewing.
Why it matters: imported fill can carry a different site history.Land use, applicable soil factors and source conditions determine the Schedule 3.1 soil standard. Municipal zoning does not automatically establish CSR land use.
The same concentration can screen differently under residential, commercial, or industrial assumptions.
Organize measurements by area and sample, with detected results and non-detect reporting limits. Samples are never averaged. CSV imports are validated before they change saved data.
Soil measurements are compared against soil standards. Groundwater protection factors still use soil concentrations; water samples are excluded.
Values close to a threshold deserve careful review. The tool does not assign a separate borderline category.
It means the lab did not detect the substance above its reporting limit. This tool does not evaluate non-detect qualifiers or reporting limits; leave the measurement blank and seek appropriate interpretation.
This tool simplifies it into an educational screening interface.
This badge signals the dataset version used by the tool, but users should always verify against official BC regulations before professional use.
Use official BC resources for regulatory decisions and professional work.